Determination of polycyclic aromatic hydrocarbons by liquid chromatography–electrospray ionization mass spectrometry using silver nitrate as a post-column reagent

Liquid chromatography–electrospray ionization mass spectrometry (LC–ESI-MS) using silver nitrate as a post-column reagent has been used for the determination of 10 polycyclic aromatic hydrocarbons (PAHs) in river water. In this method, after all the PAHs were separated by reversed-phase liquid chrom...

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Veröffentlicht in:Journal of Chromatography A 2001-08, Vol.928 (1), p.53-61
Hauptverfasser: Takino, Masahiko, Daishima, Shigeki, Yamaguchi, Kenji, Nakahara, Taketoshi
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container_title Journal of Chromatography A
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creator Takino, Masahiko
Daishima, Shigeki
Yamaguchi, Kenji
Nakahara, Taketoshi
description Liquid chromatography–electrospray ionization mass spectrometry (LC–ESI-MS) using silver nitrate as a post-column reagent has been used for the determination of 10 polycyclic aromatic hydrocarbons (PAHs) in river water. In this method, after all the PAHs were separated by reversed-phase liquid chromatography, analytes formed complexes with silver cation by mixing with silver nitrate solution. The complexes then transfer the molecular ion, [M] +, of the PAHs by charge transfer using in source collision-induced dissociation. The positive ion ESI mass spectra of all PAHs tested in this study showed [M] + as the base peak and abundant [M+Ag] +, [2M+Ag] + with very weak or no [2M+Ag] +. For the sample extraction, several solid-phase extraction parameters using the blue-chitin column were optimized. The limits of detection ( S/ N=3) of all PAHs for the spiked river water sample ranged from 0.001 to 0.03 ng/ml, and the detector responses were linear up to 1 ng/ml (correlation coefficients ≥0.0998). Repeatability and reproducibility were in the range from 4.3 to 6.8% and from 6.2 to 9.5%, respectively.
doi_str_mv 10.1016/S0021-9673(01)01127-X
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In this method, after all the PAHs were separated by reversed-phase liquid chromatography, analytes formed complexes with silver cation by mixing with silver nitrate solution. The complexes then transfer the molecular ion, [M] +, of the PAHs by charge transfer using in source collision-induced dissociation. The positive ion ESI mass spectra of all PAHs tested in this study showed [M] + as the base peak and abundant [M+Ag] +, [2M+Ag] + with very weak or no [2M+Ag] +. For the sample extraction, several solid-phase extraction parameters using the blue-chitin column were optimized. The limits of detection ( S/ N=3) of all PAHs for the spiked river water sample ranged from 0.001 to 0.03 ng/ml, and the detector responses were linear up to 1 ng/ml (correlation coefficients ≥0.0998). 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subjects Analysis methods
Analytical chemistry
Applied sciences
Chemistry
Chromatographic methods and physical methods associated with chromatography
Chromatography, Liquid - methods
Exact sciences and technology
Indicators and Reagents - chemistry
Natural water pollution
Other chromatographic methods
Pollution
Polycyclic Compounds - analysis
Polynuclear aromatic hydrocarbons
Reproducibility of Results
Sensitivity and Specificity
Silver nitrate
Silver Nitrate - chemistry
Spectrometry, Mass, Electrospray Ionization - methods
Water treatment and pollution
title Determination of polycyclic aromatic hydrocarbons by liquid chromatography–electrospray ionization mass spectrometry using silver nitrate as a post-column reagent
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